Univ Lyon, INSA Lyon, DEEP EA7429, 69621 Villeurbanne, France; BioCo Research Group, Department of Green Chemistry and Technology, Ghent University, Belgium; Veolia Research & Innovation (VeRI), Maisons-Laffitte, France.
BioCo Research Group, Department of Green Chemistry and Technology, Ghent University, Belgium.
Sci Total Environ. 2022 Mar 1;810:151247. doi: 10.1016/j.scitotenv.2021.151247. Epub 2021 Oct 25.
The formation of hydrogen sulfide (HS) during anaerobic digestion (AD) imposes constraints on the valorisation of biogas. So far, inorganic sulfur compounds -mainly sulfate - have been considered as the main contributors to HS formation, while the contribution of organic sulfur compounds is mostly neglected. This study investigates the fate of organic and inorganic sulfur compounds during two-stage anaerobic digestion with intermediate thermal hydrolysis for treatment of primary and secondary sludge in a WWTP treating domestic wastewater. The results of a seven-week monitoring campaign showed an overall decrease of organic sulfur compounds in both stages of anaerobic digestion. Further fractionation of organic sulfur revealed a high conversion of the particulate organic fraction during the first digestion stage and of the soluble organic fraction during the second digestion stage. The decrease of soluble organic sulfur during the second digestion stage was attributed to the solubilisation and hydrolysis of sulfur-containing organic compounds during thermal hydrolysis. In both digestion stages, more organic sulfur was taken up than particulate inorganic sulfur (metal sulfide) was produced, indicating the formation of other reduced sulfur forms (e.g. HS). Further batch experiments confirmed the role of organic sulfur uptake in the formation of HS during anaerobic digestion as sulfate reduction only partly explained the total sulfide formed (HS in biogas and precipitated FeS). Overall, the conversion of organic sulfur was demonstrated to play a major role in HS formation (and thus the biogas quality), especially in case of thermal hydrolysis pretreatment.
在厌氧消化(AD)过程中硫化氢(HS)的形成对沼气的增值利用构成了限制。到目前为止,无机硫化合物 - 主要是硫酸盐 - 一直被认为是 HS 形成的主要贡献者,而有机硫化合物的贡献大多被忽视。本研究调查了在处理生活污水的 WWTP 中,采用中间热解的两段式厌氧消化过程中,有机和无机硫化合物的命运。为期七周的监测活动的结果表明,在两段厌氧消化过程中,有机硫化合物总体呈下降趋势。进一步对有机硫的分级表明,在第一消化阶段,颗粒有机部分的转化率很高,而在第二消化阶段,可溶性有机部分的转化率很高。第二消化阶段可溶性有机硫的减少归因于热解过程中含硫有机化合物的溶解和水解。在两个消化阶段,有机硫的吸收量都高于颗粒状无机硫(金属硫化物)的产生量,这表明形成了其他还原硫形式(例如 HS)。进一步的分批实验证实了有机硫吸收在厌氧消化过程中形成 HS 的作用,因为硫酸盐还原仅部分解释了形成的总硫化物(沼气中的 HS 和沉淀的 FeS)。总的来说,有机硫的转化被证明在 HS 的形成(以及沼气质量)中起着主要作用,特别是在热解预处理的情况下。